CN103446830B - 烟气净化系统 - Google Patents
烟气净化系统 Download PDFInfo
- Publication number
- CN103446830B CN103446830B CN201310274800.8A CN201310274800A CN103446830B CN 103446830 B CN103446830 B CN 103446830B CN 201310274800 A CN201310274800 A CN 201310274800A CN 103446830 B CN103446830 B CN 103446830B
- Authority
- CN
- China
- Prior art keywords
- gas
- flue gas
- adsorption tower
- adsorption
- air inlet
- Prior art date
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- UGFAIRIUMAVXCW-UHFFFAOYSA-N carbon monoxide Chemical compound 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[O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims abstract description 154
- 239000003546 flue gases Substances 0.000 title claims abstract description 154
- 239000007789 gases Substances 0.000 claims abstract description 158
- 239000003570 air Substances 0.000 claims abstract description 96
- OKTJSMMVPCPJKN-UHFFFAOYSA-N carbon Chemical compound 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[C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 87
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 81
- 238000001816 cooling Methods 0.000 claims abstract description 26
- 239000000571 coke Substances 0.000 claims abstract description 20
- 238000003860 storage Methods 0.000 claims description 82
- 239000000428 dust Substances 0.000 claims description 60
- 238000000746 purification Methods 0.000 claims description 59
- 238000006477 desulfuration reactions Methods 0.000 claims description 47
- 230000003009 desulfurizing Effects 0.000 claims description 47
- 238000007599 discharging Methods 0.000 claims description 35
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- 239000003595 mist Substances 0.000 description 4
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitric oxide Chemical compound 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O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 4
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound 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- 229910052815 sulfur oxides Inorganic materials 0.000 description 1
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Abstract
Description
技术领域
[0001] 本发明涉及一种烟气净化系统,特别是涉及一种用于炼铁厂金属制造中的烧结工艺或者火力发电厂的化石燃料(煤炭)/焦炭或其化合物的燃烧过程中产生、排放的烟气,或者工业/生活废料焚烧时所排放的烟气的净化系统。
背景技术
[0002] 炼铁厂金属制造中的烧结工艺或者火力发电厂的化石燃料(煤炭)/焦炭或其化合物的燃烧过程中产生、排放的烟气中,或者工业/生活废料焚烧时所排放的烟气中,所含有的SOx (硫氧化物)、Ν0χ (氮氧化物)、重金属(含贡的重金属)、二嚼英/呋喃等污染源,对环境造成了严重的污染。为了减少上述烟气对环境的污染,现有技术采用的是干式烟气净化系统,在该系统中,烟气依次通过静电除尘器、布袋除尘器、脱硫设备和脱硝设备处理后,上述污染物被有效去除,达到了保护环境的目的。
[0003] 该系统是使用活性炭或活性焦对烟气进行净化的,但由于烟气本身具有较高的温度,再加上烟气通过风机绝热压缩后被二次加热,当进入吸附塔的烟气温度超过150°C时,会使吸附塔内的活性炭或活性焦产生局部热点,如果烟气温度持续超过150°C,使热点产生火点,活性炭或活性焦会继续氧化,使活性炭或活性焦失效甚至燃烧,从而造成吸附塔损坏。
发明内容
[0004] 本发明要解决的技术问题是提供一种烟气净化系统,也称为合成烟气净化系统(Synthetic Flue Gas Purificat1n System),略写为S-FGPS,该系统采用活性炭或活性焦对烟气进行净化处理,能够避免吸附塔内的活性炭或活性焦产生局部热点,保证系统正常工作。
[0005] 本发明烟气净化系统,包括前处理系统、烟气冷却系统和吸附塔,烟气通过管道经前处理系统进入吸附塔后被净化,所述烟气冷却系统安装在前处理系统和吸附塔之间的管路上,所述烟气冷却系统包括烟气冷却器、外气稀释器、第一温度传感器和第二温度传感器,第一烟气管为前处理系统和吸附塔之间的管路,所述第一烟气管的一端固定安装在吸附塔的进气口上,所述吸附塔的进气口上安装有进气挡板,第一烟气管的另一端与前处理系统连接,所述外气稀释器安装在第一烟气管上,所述烟气冷却器也安装在第一烟气管上,且烟气冷却器位于外气稀释器与吸附塔之间,所述第一温度传感器和第二温度传感器均安装第一烟气管上,且第一温度传感器位于外气稀释器和烟气冷却器之间,第二温度传感器位于烟气冷却器与吸附塔之间,所述外气稀释器的外气进气口上安装有能够调节进气量的挡板。
[0006] 本发明烟气净化系统,其中所述前处理系统包括静电除尘器和第一袋式除尘器,第一烟气管与第一袋式除尘器的出口连接,静电除尘器的进口与烟气排放口连接,吸附塔的出气口与烟囱连通,烟气净化系统还包括第二烟气管,第二烟气管的一端连接在静电除尘器和第一袋式除尘器之间的前处理烟气管道上,第二烟气管的另一端与烟囱连接,第二烟气管上安装有主挡板,第一烟气管上也安装有主挡板,第一烟气管上的主挡板位于外气稀释器与前处理烟气管道和第二烟气管连接处之间。本发明烟气净化系统,其中所述烟气冷却器包括壳体和喷淋管,壳体的上端开设有进气口,壳体的下端开设有出气口,喷淋管安装在壳体内,喷淋管上安装有若干喷嘴,喷嘴的出口均朝下,所述喷嘴能够喷出水滴和压缩空气的混合物,水滴的直径小于60微米。
[0007] 本发明烟气净化系统,还包括第三温度传感器,所述第三温度传感器安装在吸附塔内。
[0008] 本发明烟气净化系统,其中所述吸附塔包括至少一个吸附模块、至少一个顶部储料罐和至少一个底部出料罐,每个吸附模块均包括顶部储料仓、脱硝室、脱硫室和底部储料仓,脱硝室位于脱硫室上方,脱硝室与脱硫室之间设置有进氨室,进氨室的底部与脱硫室的顶部相连通,进氨室内设置有至少一个第一进气落料装置,脱硝室与脱硫室之间通过第一进气落料装置连通,第一进气落料装置包括上斗、下斗和连接管,上斗和下斗均呈上大下小的漏斗形,上斗的上端开口与脱硝室的底部连通,下斗套装在上斗上,下斗与上斗之间设有间隙,下斗的下端开口与连接管的上端连通,连接管的下端与脱硫室的顶部连通,底部储料仓位于脱硫室下方,底部储料仓与脱硫室之间设置有底室,底室内设置有至少一个第二进气落料装置,第二进气落料装置与第一进气落料装置结构相同,底部储料仓与脱硫室之间通过第二进气落料装置连通,第二进气落料装置的上斗的上端开口与脱硫室的底部连通,第二进气落料装置的连接管的下端与底部储料仓连通,顶部储料仓位于脱硝室的上方,脱硝室的上部设置有至少一个落料漏斗,落料漏斗的上端与顶部储料仓连通,落料漏斗的下端开口位于脱硝室的上部,顶部储料罐位于顶部储料仓上方,且与顶部储料仓连通,底部出料罐位于底部储料仓下方,且与底部储料仓连通,顶部储料罐与吸附塔的进料口连接,底部出料罐与吸附塔的出料口连接,在底室的底端开设有烟气进口,在进氨室上开设有氨气喷射装置,在脱硝室的顶部开设有烟气出口,烟气进口与吸附塔的进气口连通,烟气出口与吸附塔的出气口连通。
[0009] 本发明烟气净化系统,其中所述吸附塔包括吸附模组和支架,吸附模组包括至少一个吸附模块组、至少I个顶部储料罐和至少I个底部出料罐,吸附模块组包括4个吸附模块,4个吸附模块分为上下两层,每层2个,同层相邻的吸附模块两两之间左右固定连接,上下两层吸附模块之间也固定连接,下层的两个吸附模块的底部通过一个固定件和至少I个活动件与支架连接,所述活动件位于固定件的四周,固定件形成固定连接点,活动件形成活动连接点,所述活动件的上下两部分能够在水平面上相对移动,每个所述吸附模块的顶部储料仓均通过4根第二顶部进料管与I个分料器的四个出料口连接,每个分料器进料口均通过I根第一顶部进料管与顶部储料罐连接,每个吸附模块的底部储料仓均通过料管与底部出料罐连接。
[0010] 本发明烟气净化系统,其中所述吸附模组包括两个吸附模块组,两个吸附模块组前后设置,两个吸附模块组之间设置进气管和出气管,进气管的一端与吸附塔的进气连接,进气管的另一端与每个吸附模块的烟气进口连接,出气管的一端与每个吸附模块的烟气出口连接,出气管的另一端与吸附塔的出气口连通。吸附模组为两个以上时,吸附模组两两之间左右并排设置,考虑到热膨胀,两两相邻的吸附模组之间存在间隙。
[0011] 本发明烟气净化系统,其中吸附模块的烟气进口和烟气出口上分别安装有个别挡板C和个别挡板D,个别挡板C的下端和个别挡板D的上端均铰接在吸附模块的侧壁上,个别挡板C的上部通过连杆机构与一个气缸G的活塞杆连接,气缸G能够驱动个别挡板C封闭烟气进口,个别挡板D的下部也通过连杆机构与另一个气缸G的活塞杆连接,另一个气缸G能够驱动个别挡板D封闭烟气出口。
[0012] 本发明烟气净化系统,还包括再生塔和激活装置,所述吸附塔的底部出料罐与激活装置的进料口连接,所述激活装置的出料口与再生塔的进料口连接,所述再生塔的出料口与吸附塔的顶部储料罐连接,所述激活装置包括壳体、移送装置和添加剂喷淋管,所述添加剂喷淋管位于移送装置的上方,所述添加剂喷淋管喷淋的药剂为尿素化合物。
[0013] 本发明烟气净化系统,还包括新鲜活性炭储料仓,所述新鲜活性炭储料仓的出料口与再生塔的进料口连通。通过将新鲜活性炭储料仓连接至再生塔的进料口,能够去除新鲜活性炭内的水分和挥发份,增加其活性官能团。
[0014] 本发明烟气净化系统,还包括除尘系统,所述除尘系统包括第一、第二、第三除尘装置和第二袋式除尘器,第一除尘装置安装在激活装置和吸附塔之间,第二除尘装置安装在吸附塔的进料口上,第三除尘装置安装在再生塔的进料口处,第一、第二、第三除尘装置结构相同,均包括筒状壳体、进气口、进料管、出气口和出料口,进气口开设在壳体的下部,出气口开设在壳体的顶部,出料口开设在壳体的底部,进料管安装在壳体的上部,进料管的出料口与壳体内腔连通,进料管的进料口与吸附塔的底部出料罐连接,出料口与激活装置的进料口连接,出气口通过风机与第二袋式除尘器连接,进气口与外界大气连通。
[0015] 本发明烟气净化系统,其中所述除尘系统还包括若干吸尘罩,所述吸尘罩安装在运输轨道的顶部,所述运输轨道为运输活性炭或活性焦的轨道,所述吸尘罩通过管路与所述袋式除尘器连接。
[0016] 本发明烟气净化系统,其中所述前处理系统包括静电除尘器和第一袋式除尘器,所述静电除尘器为一次除尘装置,第一袋式除尘器为二次除尘装置。
[0017] 本发明烟气净化系统,其中所述吸附塔使用的活性炭是由重量百分百为褐煤80%和烟煤20%跟焦油进行配合后,经过炭化处理,最终经活化处理而制成。
[0018] 本发明烟气净化系统,其中所述吸附塔内烟气流经脱硫室和脱硝室的流速为0.2-0.3m/sec。
[0019] 本发明烟气净化系统与现有技术不同之处在于本发明通过设置烟气冷却系统,在向吸附塔内通入烟气的第一烟气管上安装烟气冷却器、外气稀释器、第一温度传感器、第二温度传感器,通过第一温度传感器检测进入第一烟气管内的烟气温度,并通过烟气冷却器和外气稀释器对温度过高的烟气进行冷却,然后通过第二温度传感器检测冷却后的烟气温度,保证进入吸附塔内的烟气不超过活性炭或活性焦工作的临界温度,从而能够有效的避免吸附塔内的活性炭或活性焦产生局部热点,避免活性炭或活性焦失效、燃烧,损坏吸附土it
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[0020] 本发明烟气净化系统,通过设置第二烟气管,当烟气经烟气冷却器和外气稀释器降温后,仍然超过临界温度时,直接通过第二烟气管将过热烟气排出,避免过热烟气进入吸附塔。通过在烟气冷却器的喷淋管上设置喷嘴,喷嘴将水滴和压缩空气的混合物向下喷出,使冷却水形成小于60微米的细小水滴,与从上端的进气口进入的烟气混合,混合物中的水滴能够起到给烟气降温的作用,水滴在给烟气降温的同时,受热后完全蒸发,从而不会导致吸附塔或烟气输送管道受到腐蚀。通过在吸附塔内安装第三温度传感器,能够直接检测到活性炭或活性焦的温度,避免活性炭或活性焦出现热点。
[0021] 下面结合附图对本发明的烟气净化系统作进一步说明。
附图说明
[0022]图1为本发明烟气净化系统的结构示意图;
[0023]图2为本发明烟气净化系统中吸附模块的结构示意图;
[0024]图3a为本发明烟气净化系统中吸附塔的结构示意图;
[0025]图3b为本发明烟气净化系统中附模块与支架的连接示意图;
[0026]图4a为本发明烟气净化系统中吸附模块的进出气挡板结构示意图;
[0027] 图4b为本发明烟气净化系统中吸附模块的进出气挡板的立体图;
[0028] 图5a为本发明烟气净化系统中吸附模块的进出气挡板的立体图(放大);
[0029]图5b为本发明烟气净化系统中吸附模块的进出气挡板结构示意图(放大);
[0030]图6为本发明烟气净化系统中除尘系统的除尘装置的结构示意图;
[0031]图7为本发明烟气净化系统中除尘系统的活性炭输送轨道除尘示意图;
[0032]图8为本发明烟气净化系统的烟气冷却系统的示意图;
[0033]图9为本发明烟气净化系统的活性炭脱硫能力曲线图。
具体实施方式
[0034] 烟气净化系统,是将炼铁厂烧结工艺或者煤炭火力发电厂的化石燃料及其化合物燃烧时产生的烟气中,或者焚烧炉排放的烟气中,所含有的硫氧化物、氮氧化物、贡、二噁英/呋喃以及粉尘捕集并去除的综合系统,如图1所示,本发明烟气净化系统包括前处理系统、烟气冷却系统和吸附塔、再生塔6和激活装置5、除尘系统和新鲜活性炭储料仓40,烟气通过管道经前处理系统进入吸附塔4后被净化,净化后的烟气由烟囱7排出。
[0035] 本发明的前处理系统包括静电除尘器I和第一袋式除尘器2,静电除尘器I为一次除尘装置,第一袋式除尘器2为二次除尘装置。烟气中含有的密度3-5g/Nm3的粉尘,由静电除尘器I通过施加正高电压来产生的电晕放电将密度降到40mg/Nm3以下后捕集。烟气由后端的引风机(Ia)抽吸并送到静电除尘器I中。烟气由静电除尘器I初步去除粉尘后,由后端的增压风机2b抽吸并送到袋式除尘器2中。
[0036] 碱以及氯化物所产生的微细粉尘、以气体状态存在的碱盐和S03&其他粘性粉尘等微细粉尘及其混合污染物质,通过袋式除尘器的前端用定量喷射装置2d喷射中和剂等方式,进行捕集、中和并去除。中和剂使用石灰石粉或石灰石溶液。
[0037] 用第一袋式除尘器2进行二次粉尘去除时,为了提高捕集效率,经过滤器的流速通常维持0.8-1.3m/sec,优选的流速是0.9-1.lm/sec。
[0038]由第一袋式除尘器2捕集并去除的微细粉尘及污染物质,被捕捉到的污染源通过已设置的程序用压缩空气的空气脉冲,从除尘器中分开并落下,由底部的输送装置及收集装置另作处理,一部分则通过路径(2f)送至第一袋式除尘器2的前端的进气口再次使用。
[0039] 当烟气进入吸附模块时的温度超过150° C时,高温使吸附模块内部的活性炭维持在过热状态,引发“热点”等紧急状况,会影响吸附模块的安全性及耐久性,所以需要通过烟气冷却系统将烟气的进气温度降到150° C以下。
[0040] 烟气冷却系统安装在前处理系统和吸附塔之间的管路上,结合图8所示,烟气冷却系统包括烟气冷却器3、外气稀释器2c、第一温度传感器11、第二温度传感器12、第三温度传感器、第一烟气管13和第二烟气管2e。烟气经过前处理工艺之后,可能影响到吸附塔性能和效率的粉尘已被去除,该烟气随后由增压风机2b前端的负压和后端的正压通过第一烟气管13送到烟气冷却器3中。第一烟气管13的一端固定安装在吸附塔4的进气口,吸附塔4的进气口上安装有进气挡板,进气挡板可以调节进气口的进气量,第一烟气管13的另一端与袋式除尘器2的出气口连通,外气稀释器2c安装在第一烟气管13上,烟气冷却器3也安装在第一烟气管13上,且烟气冷却器3位于外气稀释器2c与吸附塔4之间,第一温度传感器11和第二温度传感器12均安装第一烟气管13上,且第一温度传感器11位于外气稀释器2c和烟气冷却器3之间,第二温度传感器12位于烟气冷却器3与吸附塔4之间,第三温度传感器安装在吸附塔4内。外气稀释器2c的外气进气口上安装有能够调节进气量的挡板。第二烟气管2e的一端连接在静电除尘器I和第一袋式除尘器2之间的前处理烟气管道上,第二烟气管2e的另一端与烟囱7连接,第二烟气管2e上安装有主挡板,第一烟气管13上也安装有主挡板,第一烟气管13上的主挡板位于外气稀释器2c与前处理烟气管道和第二烟气管2e连接处之间。本发明中的烟气冷却器3包括壳体和喷淋管,壳体的上端开设有进气口,壳体的下端开设有出气口,喷淋管安装在壳体内,喷淋管上安装有若干喷嘴,喷嘴的出口均朝下,喷嘴能够喷出水滴和压缩空气的混合物,其中水滴的直径小于60微米。
[0041 ] 上述烟气冷却系统对烟气进行冷却时,按照下列步骤进行:
[0042] 1、使烟气从第一烟气管13进入吸附塔4内;
[0043] 2、当第一温度传感器11检测到的烟气温度不超过150°C时,关闭外气稀释器2c的外气进气口,同时烟气冷却器3不对烟气进行冷却;
[0044] 3、当第一温度传感器11检测到的烟气温度超过150°C时,烟气冷却器3启动,使第二温度传感器12检测到的烟气温度不超过150°C ;
[0045] 4、当第二温度传感器12检测到的烟气温度超过150°C时,应继续启动烟气冷却器3,并同时打开外气稀释器2c的进气口向第一烟气管13内补充外气,对烟气稀释降温,使第二温度传感器12检测到的烟气温度不超过150°C。
[0046] 在步骤4中,通过控制外气稀释器2c进气口的挡板的开启大小,来控制进入第一烟气管13的外气,使第二温度传感器12检测到的烟气温度略低于150°C。如果烟气冷却器3与外气稀释器2c均开启后,第二温度传感器12检测到的温度仍然持续超过150°C时,关闭第一烟气管13上的主挡板,打开第二烟气管2e上的主挡板,使烟气从第二烟气管2e直接排入烟囱7,同时打开外气稀释器2c、关闭烟气冷却器3,使外气通过第一烟气管13进入吸附塔4。
[0047] 附图8中是应用本发明的烟气冷却系统对烟气温度进行调节的实例。
[0048] 以炼铁厂烧结烟气为例,温度上升的原因有两种,第一种,烧结机中因做工时的设备运转及原材料条件而导致温度上升,第二种,由烧结机排出的烟气在经过静电除尘器及袋式除尘器的过程中由两台送风机绝热压缩,导致温度上升。
[0049] 通常,烟气温度最高上升至150° C的时候,第一温度传感器11检测出异常温度,烟气冷却器3通过喷水滴与压缩空气的混合物来降低烟气温度,第二温度传感器12确认,保证送到吸附塔4中烟气温度已降到150° C以下,使烟气经过正常的烟气处理过程。喷射用水通过烟气冷却器3内安装的高压输送泵在喷嘴内与压缩空气混合后,靠此压力以小于60微米的水滴喷出来,并冷却烟气,而且不会导致吸附塔4或烟气输送管路受到腐蚀等影响。
[0050] 如果烟气冷却系统检测到进入吸附塔4的烟气温度最高达到200° C的情况时,也能通过烟气冷却系统将其冷却到正常温度。该冷却系统通过烟气冷却器3初步(第一次)降低温度,然后第二次通过外气稀释器2c进一步降低温度。
[0051] 对炼铁厂烧结烟气来讲,工作时本系统的进气温度条件通常是90 - 180° C,最高
200。 Co
[0052] 为了有效应对不同的温度条件并有效地运用本烟气冷却系统,使用步骤具体如下:
[0053] 步骤一:吸附塔4前端的烟气冷却器3中的水冷过程。吸附塔4前端的第一温度传感器检测到的温度超过150° C时,作为第一步骤,用吸附塔前端的烟气冷却器3开始喷射气水混合物。水冷的设计目的是,通过微小的水滴将烟气温度冷却至150° C以下。耗水量的变化与实际温度和设计温度之间的温差成比例。
[0054] 步骤二:为与步骤一同步的、袋式除尘器2后端的外气稀释过程。烟气冷却器3中经过水冷后,吸附塔4前端的第二温度传感器12检测到的温度却始终没有降下来,在这种情况下,作为第二步骤,用袋式除尘器2后端的外气稀释器2c补充进行外气稀释作业。第二温度传感器12检测到的温度超过150° C时,立即对外气稀释器2c的进气挡板进行调整,以便通过外气稀释器2c引进外气并与烟气进行混合。
[0055] 步骤三:紧急状况时通过第二烟气管2e直接将高温烟气至烟囱,并且只许外气引入吸附塔中。经过水冷及外气稀释过程后,吸附塔前端第二温度传感器12检测到的温度下降还是不够充分,继续维持在150° C以上,在这种情况下,需要通过袋式除尘器2前方的第二烟气管2e将高温烟气直接输送至烟囱,而且只许外气通过外气稀释器2c引入吸附塔4中,以防止吸附塔过热。
[0056] 步骤四:恢复至正常运行。吸附塔前端第二温度传感器12检测到的温度低于150° C时,旁路运行模式将恢复至正常运转方式。
[0057] 当烟气温度上升微乎其微并且短期间内有间歇性的,只使用外气稀释器,用它引入外气,与烟气稀释后降低温度。
[0058] 结合图2所示,本发明中吸附塔4包括一个吸附模块、一个顶部储料罐4s和一个底部出料罐4k,吸附模块均包括顶部储料仓4c、脱硝室4b、脱硫室4a和底部储料仓41,脱硝室4b位于脱硫室4a上方,脱硝室4b与脱硫室4a之间设置有进氨室4g,进氨室4g的底部与脱硫室4a的顶部相连通,进氨室4g内设置有4个第一进气落料装置4h,脱硝室4b与脱硫室4a之间通过4个第一进气落料装置4h连通,每个第一进气落料装置4h均包括上斗4hl、下斗4h2和连接管4h3,上斗4hl和下斗4h2均呈上大下小的漏斗形,上斗4hl的上端开口与脱硝室4b的底部连通,下斗4h2套装在上斗4hl上,下斗4h2与上斗4hl之间设有间隙,以便于烟气从上斗4hl和下斗4h2之间的间隙进入活性炭或活性焦颗粒的间隙。下斗4h2的下端开口与连接管4h3的上端连通,连接管4h3的下端与脱硫室4a的顶部连通,从而使活性炭从脱硝室4b经第一进气落料装置4h进入脱硫室4a内,并且脱硫室4a上部的烟气经过进氨室4g后,能够通过上斗4hl和下斗4h2之间的间隙进入脱硝室4b内。
[0059] 底部储料仓41位于脱硫室4a下方,底部储料仓41与脱硫室4a之间设置有底室4e,底室4e内设置有4个第二进气落料装置4f,第二进气落料装置4f与第一进气落料装置4h结构相同,底部储料仓41与脱硫室4a之间通过第二进气落料装置4f连通,第二进气落料装置4f的上斗的上端开口与脱硫室4a的底部连通,第二进气落料装置4f的连接管的下端与底部储料仓41连通,以使烟气从第二进气落料装置4f的上斗和下斗之间的间隙进入脱硫室4a内。
[0060] 顶部储料仓4c位于脱硝室4b的上方,脱硝室4b的上部设置有4个落料漏斗4n,落料漏斗4n的上端与顶部储料仓4c连通,落料漏斗4n的下端开口位于脱硝室4b的上部,以使顶部储料仓4c内的活性炭能够经落料漏斗4n进入脱硝室4b内。顶部储料罐4s位于顶部储料仓4c上方,且与顶部储料仓4c连通。底部出料罐4k位于底部储料仓41下方,且与底部储料仓41连通,顶部储料罐4s与吸附塔的进料口连接,底部出料罐4k与吸附塔的出料口连接。在底室4e的底端开设有烟气进口 4d,在进氨室4g上开设有氨气喷射装置,在脱硝室4b的顶部开设有烟气出口 4i,烟气进口 4d与吸附塔4的进气口连通,烟气出口 4i与吸附塔4的出气口连通。
[0061] 烟气经烟气冷却系统调至吸附塔内最佳处理温度范围之后,通过进气口进入吸附塔4内吸附模块的烟气进口 4d,在底室4e由分布均匀的4个第二进气落料装置4f的上斗和下斗之间的间隙,送到脱硫室4a的脱硫层。在脱硫层停留的时间根据烟气的性状有些差异,最佳经过流速为0.2-0.3m/sec且进气浓度为150-220ppm时,需要4_7秒的停留时间,当进气浓度大于150-220ppm时,需要更长的停留时间,如果超过该流速0.2-0.3m/sec时,活性炭本身的粉尘会飞散并混合到烟气中,会污染净化的烟气,另外,流速增加会导致活性炭层的差压增大。在脱硫层,由活性炭或活性焦的吸附功能去除硫氧化物、贡、二噁英/呋喃等污染源。
[0062] 烟气从脱硫层出来之后,经第一进气落料装置4h进入脱硝室4b的脱硝层,由活性炭通过催化功能将氮氧化物去除。具体来说,烟气从脱硫层出来,在模块的进氨室4g中与氨气进行混合,然后进入脱硝层的底部。氨是以气体状态从氨储罐4w排出,在雾化器4x中与蒸汽进行热交换并升温,然后在混合器4x’中跟另一种方式升温的外气相互混合,然后在模块的进氨室4g通过氨气喷射装置喷出后与烟气进行混合。氨的喷淋量由氨和氮氧化物的当量比来决定,没有能够与氮氧化物引起反应的剩余氨需要进行调节,以免超过环境容许范围内的标准值。在脱硝层停留的时间根据烟气的性状有些差异,最佳经过流速为0.2-0.3m/sec且进气浓度为150-220ppm时,需要6_9秒的停留时间,当进气浓度大于150-220ppm时,需要更长的停留时间。在脱硝室4b内,烟气中的氮氧化物通过活性炭的催化功能有选择性地跟氨产生化学反应,并分解成水和氮(N2),然后与净化的烟气一同经过吸附模块的烟气出口,然后由吸附塔出气口排出,最终流向烟囱7。
[0063] 为了提高吸附塔4的工作效率,相对于上述实施例的吸附塔4做如下改进。本实施例中,吸附塔4包括吸附模组和支架,吸附模组包括两个吸附模块组、I个顶部储料罐4s和4个底部出料罐4k,吸附模块组包括4个吸附模块,4个吸附模块分为上下两层,每层2个,同层相邻的吸附模块两两之间左右固定连接,上下两层吸附模块之间也固定连接,结合图3b所示,下层的两个吸附模块的底部通过一个固定件和至少I个活动件(本实施例中为5个活动件)与支架连接,活动件31位于固定件30的四周,固定件30形成固定连接点,活动件31形成活动连接点,活动件的上下两部分能够在水平面上相对移动,本实施例中固定件为螺栓,活动件为下板、支柱和滚珠轴承,下板固定安装在支架的上端面上,支柱固定安装在位于下方的吸附模块的下部,而且位于下板的上方,支柱下端以滚动方式装有滚珠轴承,滚珠轴承压在下板的上表面上。参考图2所示,每个吸附模块的顶部储料仓4c均通过4根第二顶部进料管4m与I个分料器4j的四个出料口连接,每个分料器4j均通过I根第一顶部进料管4t与顶部储料罐4s连接,每个所述吸附模块的底部储料仓41均通过料管与底部出料罐4k连接。
[0064] 如图3a所示,当处理大量烟气时,单位模块的大小通常是6m宽、6m长,最大也是
7.2m宽,7.2m长,吸附塔包括左右两个吸附模组,如果吸附模组是两个以上时,考虑到热膨胀,应留有适当的间隔,因此,本实施例中两个吸附模组之间具有一定间隙。每个吸附模组均包括两个吸附模块组,也就是一个吸附塔包括有16个吸附模块。两个吸附模块组前后设置,两个吸附模块组之间设置进气管4q和出气管4r,进气管4q的一端与吸附塔的进气连接,进气管4q的另一端与每个吸附模块的烟气进口 4d连接,出气管4r的一端与每个吸附模块的烟气出口 4i连接,出气管4r的另一端与吸附塔4的出气口连通。通过在吸附塔上只设置两个储料罐,这样大大减少了各模块拥有各自的储料罐(“一个模块,一个储料罐”)的个别调节方式在机械、操作方面的隐患。而且,活性炭进料管路和输送设备的分叉及分配装置变得更简单,距离变得最短。在每个吸附模块内均安装有第三温度传感器。在每个吸附模块的烟气进口 4d和烟气出口 4i上分别安装有个别挡板C和个别挡板D,个别挡板C的下端和个别挡板D的上端均铰接在吸附模块的侧壁上。个别挡板C的上部通过连杆机构与一个气缸G的活塞杆连接,气缸G通过连杆机构驱动个别挡板C绕铰接销轴转动,打开或封闭烟气进口 4d ;个别挡板D的下部也通过连杆机构与另一个气缸G的活塞杆连接,另一个气缸G通过连杆机构驱动个别挡板D绕铰接销轴转动,打开或封闭烟气出口 4i。本实施例中连接个别挡板C和D的连杆机构均为一个近似V形的连杆,连杆的中部铰接在个别挡板C或个别挡板D下方的吸附模块的侧壁上,连杆的上端与个别挡板C或个别挡板D的上部连接,连杆的下端与对应的气缸G的活塞杆铰接。
[0065] 吸附模块由于构造物及填充其内的活性炭的荷重而受垂直、水平荷重的影响,运转时烟气的温度使得其内部平常维持120-150° C的温度条件,因此需要考虑好荷重及热膨胀的影响,然后以最佳模块数作为其基本单位。本实施例中以8个吸附模块,即以一个吸附模组为基本单位,左右两个吸附模组之间留有膨胀节空间,通过膨胀节将两个吸附模组的进气管和出气管连接,并且将吸附模块的底部通过一个固定件和五个活动件与支架连接,把上述热膨胀对吸附塔机械性能的影响降到最低,紧急状况发生时(“热点”发生时)保证其他吸附塔免受影响的独立结构。
[0066] 为了避免在吸附塔内部发生隐患时中断整个系统的运转,采取措施并解决问题之后,再重新启动的低效率方法,本发明采取下述方法以使整个系统能够始终保持正常运转的方式。其步骤为:当第三温度传感器检测到吸附模块异常时,报警和异常符号传到中央控制室,“热点”状况得到确认后,立即将异常的吸附模块的烟气进口的个别挡板C和烟气出口的个别挡板D同时关掉。如附图4a、4b、5a、5b所示,模块的个别挡板C,D平常各安装在进口及出口的下、上端,正常运转时是打开的状态,但,如发生紧急状况,由控制个别挡板的气缸G起动个别挡板,将开口部关闭并封住烟气进出,以切断流向模块内部的气流。此外,中断异常吸附模块对活性炭的进料与出料。其他所有的吸附模块却仍在正常运转,具体来说,在个别挡板正常打开的状态下,烟气正常流动,活性炭的进料和出料也很正常。以上模块中烟气进出已被中断,但火种有可能继续氧化,因此需要注入氮气,阻止“热点”的扩大,并监测温度下降的过程。经过确认后已确定异常的吸附模块内的温度已降到正常范围而且“热点”已灭尽,该异常的吸附模块的个别挡板C,D以及活性炭的移动仍将处于关闭/中断的状态,停止注入氮。异常模块以后将通过设备维修或者在厂休期间进行确认,并采取适当的措施将其恢复原状。
[0067] 吸附塔4的底部出料罐4k与激活装置5的进料口连接,激活装置5的出料口与再生塔6的进料口连接,再生塔6的出料口与吸附塔4的顶部储料罐4s连接,激活装置5包括壳体、移送装置和添加剂喷淋管,添加剂喷淋管固定安装在壳体内,且添加剂喷淋管位于移送装置的上方,活性炭从激活装置5的进料口进入后,被移送装置(如皮带输送机)移送到激活装置5的出料口,在这个过程中,添加剂喷淋管向活性炭上喷洒药剂,添加剂喷淋管喷淋的药剂为尿素化合物。新鲜活性炭储料仓4ο的出料口与再生塔6的进料口连通。
[0068] 从吸附模块排出的活性炭到再生塔6中经过再生处理,吸附在活性炭上的硫氧化物、贡以及二噁英/呋喃等污染源成为浓缩气体;硫氧化物在硫酸制造设备6f中制成商业用硫酸,而其他污染源在废水处理设备中处理。二噁英在活性炭再生过程中,在再生塔内高温(400-450° C)和无氧气(O2)的条件下完全分解、消灭。
[0069] 在再生塔6中经过再生的活性炭,其绝大部分污染源已被解析和分解,通常不到lwt%的微量污染源残留在其中,在再生塔6的出料口处设置筛子6e,从而保证再生后的活性炭大小维持在2.8_以上,才被运输到吸附塔4中再使用。再生的活性炭与新的活性炭一同通过吸附塔顶部设置的除尘装置4u去除微细粉尘之后,贮藏在顶部储料罐4s里。活性炭靠着重力从顶部储料罐沿着与顶部储料仓4c相连接的管道往下移动,通过管路和管路上开关挡板的动作依次维持气密,然后经由模块顶部的第二顶部进料管4m进到顶部储料仓4c中。装在顶部储料仓里的活性炭进料后,在脱硝室4b通过催化功能进行脱硝(脱氮),在脱硫室4a通过吸附功能进行脱硫,这些脱硝和脱硫过程中活性炭适当地停留一段时间,然后为了再生从模块的脱硫室4a中排出。活性炭根据程序设置的时间按时从脱硫室4a中排出后,暂时存放在底部储料仓41以及底部出料罐4k中,然后用搬运装备排出。
[0070] 经激活装置5喷淋后的活性炭和从新鲜活性炭储料仓4ο供应的新鲜活性炭一同输送至再生塔6,为了再生从顶部经过升温区6a并温度升高,当温度超过300° C时开始解析。在升温区温度升到400-450° C并从活性炭解析、分解后形成的浓缩二氧化硫,与其他被解析的污染源一同经过脱气区6b,输送至硫酸制造设备6f。活性炭在脱气区完成解析后,下移到底部冷却区6c,由送风机引入的外气进行冷却,此外气在冷却活性炭的过程中通过热交换获得热源并升温,约200-250° C,在升温装置6d中再加热到500-600° C后移到升温区6a,使活性炭的温度升高,最终从再生塔送到大气中。活性炭从再生塔排出后,经过筛子6e,只有大于2.8mm的活性炭再进入吸附塔中,从筛子滤出的活性炭微粉或不到2.8mm的小颗粒另外收集后再使用。根据从系统滤除的活性炭量,从新鲜活性炭储料仓4ο中供应相同量的新鲜活性炭。
[0071] 吸附模块中的活性炭作为去除烟气中污染源的介质,需形成良性循环,换句话说,在吸附塔中通过圆滑的出料和进料将吸附塔中的污染源迅速抽出并再生,然后将再生的活性炭重新投料,而且当吸附塔内排出的活性炭停留时,为了避免结露及腐蚀等现象发生,活性炭的排出量及循环量,以炼铁厂烧结烟气中硫氧化物浓度220ppm为准,与整个模块的活性炭总量相比应该在0.15-0.2wt%范围内;活性炭输送装备的最大机械能力,与活性炭总量相比应该在0.3 - 0.4wt%范围内;硫氧化物浓度越高,循环量及输送装备的机械能力应得到相应的提高。活性炭在吸附硫氧化物等污染源的状态下,在吸附塔4、再生塔6及其他储罐中长期停留的时候,为了避免在酸露点以下结露/腐蚀等现象发生,对容器的外部采取加热装置、保温及/或用氮填充等措施,减少与氧的接触。活性炭具有高磨损性,为了避免输送装备将活性炭颗粒完全粉碎或减弱的机械磨损发生,应该选择能把摩擦降到最小的装备。通常要使用斗式输送机、柔性橡胶输送带等低磨损性输送装备。在输送活性炭的时候,前、后工艺有可能发生隐患,因此需要安装适当容量的缓冲罐以便能够提供缓冲功能;活性炭和被吸附在其中的污染源在吸附塔4、再生塔6以及其他储罐中长期停留时,对容器采取加热装置、保温及/或用氮填充等措施,以免在酸露点以下结露/腐蚀等现象发生。
[0072] 为了避免正在循环中的活性炭降低系统的性能,为了活性炭能够顺利发挥吸附及催化功能,需要将因机械磨损及化学侵蚀而产生的微粉、尺寸不到2.8mm的活性炭颗粒等不必要的、或者脱离轨道的活性炭从系统去除,因此,需要设置除尘系统。本发明的除尘系统包括第一、第二、第三除尘装置4v/4u/6h和第二袋式除尘器,第一除尘装置4v安装在激活装置5和吸附塔4之间,第二除尘装置4u安装在吸附塔的进料口上,第三除尘装置6h安装在再生塔6的进料口处。结合图6所示,第一、第二、第三除尘装置均包括筒状壳体41、进气口 42、进料口 43、出气口 44和出料口 45,进气口开设在壳体41的下部,出气口 44开设在壳体41的顶部,出料口 45开设在壳体41的底部,进料管43安装在壳体41的上部,进料管43的出料口与壳体41内腔连通。第一除尘器4v的进料管的进料口与吸附塔4的底部出料罐4k连接,出料口 45与激活装置5的进料口连接。每个除尘装置的出气口均通过风机与第二袋式除尘器连接,进气口均与外界大气连通。除尘系统还包括若干吸尘罩,吸尘罩安装在运输轨道的顶部,运输轨道为运输活性炭或活性焦的轨道,吸尘罩通过管路与袋式除尘器连接。
[0073] 如附图6所示,除尘装置中外气b引入的方向与活性炭a下落的方向相反,由此产生的活性炭飞灰与引入的外气一同沿着管路移动,送到第二袋式除尘器中。为了避免粉尘在输送时积压在输送管路上,需要除尘器用其他送风机以约20m/sec以上的速度强行输送。
[0074] 在活性炭的输送轨道经常由活性炭粉尘大量堆积,需要在漂浮的粉尘沉淀之前将其抽吸并捕集。如图7所示,装在顶部活性炭桶里的活性炭d在移动中所产生的粉尘,和空桶e之间的飞灰,通过轨道顶部的吸尘罩f捕集后,通过烟道g输送,最终送到集尘用袋式除尘器中处理。而且,以高速输送,以免在管路上粉尘堆积。不到2.8mm的活性炭颗粒在再生塔中将污染源去除后,通过筛子收集并作为燃料来再使用。脱离输送装备的微粉及活性炭颗粒,通常由输送装备的运输轨道上内置的吸尘罩来收集,如果其收集率低而且效果微乎其微的话,另设真空输送装备及管路,以便必要时能够收集多处的微粉及活性炭颗粒。
[0075] 本发明使用的活性炭是由重量百分比为褐煤80%和烟煤20%跟焦油(沥青)进行配合后,经过炭化处理,最终经过活化处理而制成的。当然,本发明也可以使用其他活性炭或活性焦。
[0076] 将现有的活性炭、本发明的活性炭以及经化学激活后的本发明的活性炭进行了对硫氧化物吸附能力的试验,并测出了吸附在活性炭中的硫氧化物。试验结果显示在附图9中。经过化学添加剂喷射后激活的本发明的活性炭对硫氧化物的吸附能力比其他两种活性炭更强。值得注意的是,本发明的活性炭激活后,在吸附和解析反复的循环中其硫氧化物吸附能力始终保持得良好,从未减退。本次试验结果表明,烟气净化系统中使用的活性炭在反复的循环工艺中其机械和化学特性逐渐减退。经化学激活后的本发明的活性炭将会提高以下功能:提高SWC (脱硫负载因子);通过保持化学基团,减少活性炭磨损;避免吸附塔内部堵塞现象发生;在吸附塔的脱硝过程中降低耗氨量。
[0077] 以上所述的实施例仅仅是对本发明的优选实施方式进行描述,并非对本发明的范围进行限定,在不脱离本发明设计精神的前提下,本领域普通技术人员对本发明的技术方案作出的各种变形和改进,均应落入本发明权利要求书确定的保护范围内。
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CN109827622A (zh) * | 2017-11-23 | 2019-05-31 | 中冶长天国际工程有限责任公司 | 活性炭烟气净化系统及其辊式给料机排料流量测量方法 |
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